Final Environmental Impact Statement
Final Environmental Impact Statement
Final Environmental Impact Statement
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Vestal <strong>Final</strong> <strong>Environmental</strong> <strong>Impact</strong> <strong>Statement</strong> Chapter 3<br />
detected hibernating at the Ventling mine. This site most likely serves as a day/night<br />
roost site for this species. Other abandoned mine sites within or around the project area<br />
most likely also provide hibernation and roosting habitat.<br />
Black-tailed Prairie Dog (R2 Sensitive Species)<br />
Suitable prairie dog habitat on the Black Hills National Forest is limited to non-rocky<br />
grassland soils on the Hell Canyon RD. In 2005, there were approximately 400 acres of<br />
prairie dog towns on the Forest consisting of about 10 active colonies (USDA Forest<br />
Service 2009). The colonies are comparatively small and disjunct from adjacent known<br />
colonies. Prairie dog towns on the Forest have remained stable or have increased despite<br />
recreational shooting and disease. All of the prairie dog towns occur within grazing<br />
allotments (District records). Black-tailed prairie dogs are found to be more abundant in<br />
heavily grazed areas than in un-grazed areas in the Black Hills of southwestern South<br />
Dakota.<br />
In South Dakota the black-tailed prairie dog’s range includes most all western counties<br />
(Higgins et al. 2000).<br />
There is an active, small prairie dog town (031303-36; Glen Erin) in the project area.<br />
This area was mapped in 2011, and is 9.3 acres.<br />
Mountain Sucker (R2 Sensitive Species, MIS)<br />
The mountain sucker occurs most often in cool, clear mountain streams with moderate<br />
water velocities. Stream substrate associated with mountain sucker habitat varies widely<br />
and ranges from mud to sand, gravel and boulders, although cobbles are most common.<br />
This species is found on the stream bottom and is closely associated with cover (exposed<br />
roots, undercut banks, log jams and boulders). Mountain suckers are benthic feeders and<br />
their diet is primarily simple plants like diatoms and green algae, but small invertebrates<br />
are also ingested. Spawning occurs in the spring, but the exact timing varies by elevation<br />
and water temperature. In the Black Hills, the spawning period for mountain suckers is<br />
probably June and maybe early July (Shearer personal communication, 2006). This<br />
species is an open substrate spawner (broadcast spawner), meaning it does not build or<br />
defend a nest or redd. The incubation period of mountain sucker embryos is thought to be<br />
short, around 8 to 14 days (Belica & Nibbelink 2006).<br />
The status of the mountain sucker in the Rocky Mountain Region and the Black Hills was<br />
assessed by Belica and Nibbelink (2006) and Isaak et al. (2003), respectively. Mountain<br />
suckers are native to the Black Hills and comprise the eastern-most range of the species.<br />
Recent surveys suggest mountain suckers occur in many of its historic drainages<br />
throughout the Black Hills (Isaak et al. 2003), but localized population reductions or<br />
absence at selected sites has occurred (USDA Forest Service 2010).<br />
The mountain sucker historically occurred in French Creek. The first recorded occurrence<br />
was in 1893 at Custer, SD (Evermann & Cox 1896). Stream surveys in French Creek in<br />
1960 found mountain suckers downstream of Stockade Lake/Dam (Stewart & Thilenius<br />
1964). French Creek upstream of Stockade Lake was not surveyed. Surveys in 1984 and<br />
1992-93 captured mountain suckers in French Creek downstream of Stockade Lake, but<br />
not upstream of the lake (Ford 1988, SDGFP 2009). SDGFP fisheries surveys in 2009 in<br />
streams within the Vestal project area did not collect any mountain suckers.<br />
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